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Although rice and corn are two main cash crops in Lombardy (North Italy) and their cultivation involves several thousands of farmers, risk assessment of pesticide exposure is rarely done, especially in small and medium sized enterprises. With the use of pads for environmental monitoring (OECD protocol), of pre- and post-exposure 24h urine collection for biological monitoring and of hand wash for hands' exposure, we measured the exposure of 28 agricultural workers to propanil and terbuthylazine in real-life working conditions. In propanil applicators, median daily exposure on the clothes was 73.5μmol per worker, while the exposure on the skin was 22.4μmol. For terbuthylazine, these exposures were 37.2μmol and 0.86μmol per worker, respectively. Median excretion of the propanil metabolite (3,4-dichloroaniline) after exposure was 84nmol in 24h urine, and 13nmol for the metabolite of terbuthylazine. Risk assessment performed by comparing to the AOELs of the applied active ingredients with an estimated internal dose, obtained based on the measured levels of skin and hand exposure and the percentage of dermal absorption of the active ingredients considered showed that 4 propanil workers, and no terbuthylazine workers, were overexposed. Our study helps define and confirm relationships between different exposure determinants, which can be used in the development of tools for risk assessment of exposure to pesticides in small and medium sized enterprises., (Copyright © 2012 Elsevier Ireland Ltd. All rights reserved.)

The evaluation of chemical risk in agriculture is complicated because of difficulties in obtaining measures representative of working conditions. This is the reason why experiences finalized at producing risk estimates are running. In this frame, a Regional working group has developed the project "Pesticide exposure and risk profiles in agriculture". Priority scenarios have been selected and the main variables correlated with pesticide exposure have been pointed out. A value for each variable has been defined. The sum of these values allows the definition of "Exposure Indices" (EI), which can be reduced by multiplication for a coefficient calculated based on use of personal protective devices, training and education and equipment conditions. A Risk Index is calculated as the product of EI per a toxicity index, calculated based on the risk phrases of the substances used ("Risk Profile"). Risk Profiles allow the production of risk estimates and the definition of the appropriate preventive interventions. Next phase will be addressed at the validation of the model, to be carried out through the determination of the levels of concordance between the risk class allocation obtained from the model and the one obtained from environmental and biological measures, in the same groups of workers.

Dicarboximide fungicides (DF) such as vinclozolin, iprodione, procymidone are widely used on vines, fruit and vegetables, and anilide herbicides (AH) such as diuron, linuron, propanil are used to control weeds on hard surfaces, such as, roads, railway tracks, paths, and in crops, forestry. Italian reports on food safety found many samples contaminated by pesticides belonging to these categories, even though only few exceeding L.M.R. Since adverse effects on human health, such as endocrine disruption, have been reported, biological monitoring is essential for exposure assessment both of occupationally exposed subjects and of the general population. Common metabolites of DF and AH are dichloroanilinines such as 3,4-DCA and 3,5-DCA, urine samples from 153 subjects living in Novafeltria, central Italy, were collected for analysis of 3,4- and 3,5-DCAs, each participant was invited to complete a very detailed questionnaire. A total of 151 out of 153 samples were found to be positive for 3,5-DCA, and 81.7% were positive for 3,4-DCA. Also 33 workers, engaged in application of propanil on rice in northern Italy, were involved in the study and 3,4-DCA was determined as marker of exposure. 3,4 and 3,5 dichloroaniline are useful and promising biological indicators for monitoring occupational and environmental exposure to these classes of pesticides.

In the present study, the personal exposure to mancozeb and/or ethilenethiourea (ETU) in 13 Italian vineyard workers and in 13 subjects without occupational exposure to pesticides was investigated. With this aim, the level of ETU in urine and the dermal exposure to mancozeb were determined. Baseline urinary ETU results were lower than the analytical limit of detection for all controls (<0.5 microg/g creatinine) and for ten workers (median <0.5, range <0.5-3.4 microg/g creatinine). In workers, urinary ETU was significantly increased at the end of shift (2.5, <0.5-95.2 microg/g creatinine) compared with baseline levels. End-shift urinary ETU was higher in operators using open tractors (n=7) than in those using closed tractors (n=5) (16.2 vs. 2.4 microg/g creatinine), but the difference was not significant (P=0.073). End-shift urinary ETU was positively correlated with dermal exposure to mancozeb determined both over the clothes and on the skin (Spearman's rho=0.770 and 0.702, P=0.009 and 0.024, respectively). Wine consumption positively influenced the excretion of ETU.